<br />MANAGEMENT BRIEF
<br />
<br />203
<br />
<br />ASMR 3
<br />
<br />ASMR 3 differs from formulations 1 and 2 in that
<br />more flexibility is allowed in the estimation of age- and
<br />time:specific capture probabilities (fi a)' As in ASMR
<br />2, U T is estimated directly; however, we use the
<br />conditional maximum likelihood estimate for the P
<br />a,l
<br />matrix, that is,
<br />
<br />^ rna,l + ra.t
<br />Pa.t = ^. ^ .
<br />. Ua,t + Ma,t
<br />
<br />This formulation eliminates the need to specify annual
<br />vulnerability schedules at the expense of a much larger
<br />parameter set. ASMR 3 maximizes equation (6) by
<br />varying e = (M'adull and Ua.T).
<br />One strength of the overall ASMR approach is that it
<br />allows the estimation of recruit abundance for years
<br />preceding the onset of data collection by using age-
<br />specific survival rates and initial-year abundance as
<br />follows:
<br />
<br />^ Ua.l
<br />U2,2-a = ~.
<br />nSj
<br />t=2
<br />
<br />This is an important aspect of the ASMR and
<br />a distinction from the "recruitment" parameter esti-
<br />mated by Jolly-Seber type methods (discussed below).
<br />
<br />Assignment of Apparent Age at First Capture
<br />
<br />We reparameterized the polynomial length-at-age
<br />relationship contained in the humpback chub Endan-
<br />gered Species Act recovery goals and based on fish
<br />collected in Grand Canyon (USFWS 2002) to a von
<br />Bertalanffy growth function necessary for the Lorenzen
<br />mortality curve. We then used the inverse von
<br />Bertalanffy growth function to assign apparent age as
<br />a function of length, that is,
<br />
<br />a=-~log,,(I-f)-ao, (11)
<br />
<br />where k=0.12, ao =0.87, and I", =455. We conducted
<br />sensitivity analyses on the effect of growth parameter
<br />misspecification on abundance and recruitment trends.
<br />
<br />Model Performance
<br />
<br />We tested the estimation methods by generating
<br />simulated capture-recapture data from known numbers
<br />of fish Ua,l and U2,t from ages 2-30 and years 1989-
<br />2002 subject to individual binomial capture, survival,
<br />and recapture events over age and time with known va.1
<br />and annual capture probabilities (fi/)' These tests
<br />indicate that the method gives unbiased estimates of
<br />the PI' Ua,l up to at least age 10, the U2,1 for all t, Va,1 for
<br />the time periods mentioned above, and age-specific
<br />survival rates Sa up to at least a = 20. The simulated
<br />
<br />(9)
<br />
<br />recruitment and initial stock estimates U2,t and Ua.l are
<br />precise (<10% error) for the period from the early to
<br />the mid 1990s and become imprecise for the late 1990s
<br />to 2002. Most S estimates are precise for all a.
<br />a
<br />We cannot assign an accurate age to each humpback
<br />chub at first capture. The recapture size data indicate
<br />that growth rates are extremely variable; for example,
<br />the average size of an age-l0 humpback chub is around
<br />300 mm TL, but fish of this size can be anywhere
<br />between about 6 and 15 years of age. When we assign
<br />a fish an "age" at first capture, that age may well be
<br />predictive of the subsequent size-dependent survival
<br />rate (Lorenzen model) but is probably not the correct
<br />age for assigning the fish to a cohort. This means that
<br />the y,7ar-class strengths or apparent cohort sizes Ua,l
<br />and U2,1 estimated by the procedure outlined above are
<br />not the numbers of fish recruiting or initially present by
<br />cohort but rather some smoothed or running average of
<br />the actual cohort strengths. The estimation method
<br />should still be able to detect longer-term trends in
<br />abundance and recruitment, but it is less able to detect
<br />subtle changes in year-class strength.
<br />The use of VP A back propagation for calculating Ua,1
<br />does not cause the ASMR method to overestimate adult
<br />abundance. To evaluate this, we replaced equation (3)
<br />with the forward prediction equation (1) for U and
<br />A 0.1
<br />included th,7 initial unmarked abundances Ua,l (a = 2, . .
<br />.,30) and U2,I (t > 1) in the set ofunIrnown parameters
<br />to be estimated by maximizing equation (6). This
<br />resulted in essentially the same abundance and adult
<br />mortality estimates as the back propagation method.
<br />While the proposed estimation method is unbiased
<br />when supplied with accurate ages at first capture, tests
<br />with simulated data lhat include initial aging error
<br />indicate lhat it produces estimates of A. and M'adUlt that
<br />are biased downward by about 7% and 11 %, re-
<br />spectively. However, it still tracks the simulated
<br />recruitment patterns over time and does not create
<br />a spurious simulated trend in back-calculated recruit-
<br />ments before lhe first year of sampling (Figure I).
<br />As a measure of uncertainty, we sampled lhe
<br />posterior distribution of the parameter estimates using
<br />Markov chain-Monte Carlo (MCMC) techniques for
<br />each ASMR formulation. Following Gelman et al.
<br />(2000), we constructed 95%-credible intervals from
<br />MCMC parameter chains of length 1,000 from 200,000
<br />MCMC trials, retaining every l00th trial and disre-
<br />garding the first half of lhe chain. We assessed
<br />convergence using Gelman and Rubin's potential scale
<br />reduction factor (R Development Core Team 2005).
<br />
<br />Discussion
<br />
<br />The abundance and mortality trends from lhe ASMR
<br />and Jolly-Seber models are similar (Coggins et al.
<br />
<br />(10)
<br />
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